Experimental Determination of Solubility Constants of Saponite at 2 Elevated Temperatures in High Ionic Strength Solutions, 3 Revision 1
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1 Experimental Determination of Solubility Constants of Saponite at 2 Elevated Temperatures in High Ionic Strength Solutions, 3 Revision 1 4 5 Yongliang Xiong1 6 7 Department of Nuclear Waste Disposal Research & Analysis, 8 Sandia National Laboratories (SNL), 1515 Eubank Boulevard SE, Albuquerque, NM 9 87123, USA 10 1 Corresponding author, e-mail: [email protected]. 1 11 12 ABSTRACT 13 Saponite occurs in a wide range of environments from hydrothermal systems on 14 the Earth to surface deposits on Mars. Of practical importance is that Mg-saponite forms 15 when glasses for nuclear waste are altered in Mg-bearing aqueous solutions. In addition, 16 saponite is favorably considered as candidate buffer materials for the disposal of high- 17 level nuclear waste and spent nuclear fuel in harsh environments. However, the 18 thermodynamic properties, especially for Mg-saponites, are not well known. Here the 19 author synthesized Mg-saponite (with nitrate cancrinite) following a previously reported 20 procedure and performed solubility experiments at 80 oC to quantify the thermodynamic 21 stability of this tri-octahedral smectite in the presence of nitrate cancrinite. Then, in 22 combination with the equilibrium constant at 80 oC for the dissolution reaction of nitrate 23 cancrinite from the literature, the author determined the solubility constant of saponite at 24 80 oC based on the solution chemistry for the equilibrium between saponite and nitrate 25 cancrinite, approaching equilibrium from the direction of supersaturation, with an 26 equilibrium constant of –69.24 ± 2.08 (2s) for dissolution of saponite at 80 oC. 27 Furthermore, the author extrapolated the equilibrium constant at 80 oC to other 28 temperatures (i.e., 50 oC, 60 oC, 70 oC, 90 oC and 100 oC) using the one-term 29 isocoulombic method. These equilibrium constants are expected to find applications in 30 numerous fields. For instance, according to the extrapolated solubility constant of 31 saponite at 50 oC and 90 oC, the author calculated the saturation indexes with regard to 32 saponite for the solution chemistry from glass corrosion experiments at 50 oC and 90 oC 33 from the literature. The results are in close agreement with the experimental 2 34 observations. This example demonstrates that the equilibrium constants determined in 35 this study can be used for reliable modeling of the solution chemistry of glass corrosion 36 experiments. 37 3 38 INTRODUCTION 39 40 Saponite, a tri-octahedral smectite, occurs in a wide range of environments. For 41 instance, it occurs in igneous rocks as hydrothermal alteration products (e.g., Kohyama et 42 al., 1973; April and Keller, 1992; Garvie and Metcalf, 1997), and in metamorphosed 43 dolomitic limestone as hydrothermal products (e.g., Post, 1984). It also occurs as lake 44 sediments and in volcanic rocks on seafloor (e.g., Desprairies et al., 1989; Cuevas et al., 45 2003; Kadir and Akbulut, 2003). Its occurrence in the Martian meteorites and its 46 proposed occurrence in Mawrth Vallis region and Yellowknife Bay, Gale Crater on Mars 47 (e.g., Bishop et al., 2013; Hicks et al., 2014; Bristow et al., 2015) generated enormous 48 scientific interest. Most recently, saponite was also observed in an analog study of the 49 hydrothermal alteration in the martian subsurface (e.g., Sueoka et al., 2019; Calvin et al., 50 2020). 51 Additionally, of practical importance and therefore particular interest is that 52 saponite is relevant to the geological disposal of nuclear waste, as Mg-saponite has been 53 observed as an alteration product when a borosilicate glass for nuclear waste is corroded 54 (Thien et al., 2010) in Mg-containing solutions, as detailed below. 55 Mg-bearing groundwaters are common in the disposal concepts in various rock 56 formations. For instance, salt formations have been recommended for nuclear waste 57 isolation since the 1950’s by the U.S. National Academy of Science (1957). Because of 58 their excellent properties of high heat conduction, low permeability and a propensity to 59 self-seal, rock salt is a viable candidate for a nuclear waste repository. Salt formations 60 contain brines, which have relatively high concentrations of magnesium (Nishri et al., 4 61 1988; Schussler et al., 2001; Xiong and Lord, 2008). For instance, the Q-brine at Asse, 62 Germany, has a magnesium concentration of 4.47 mol•kg–1 (Nishri et al., 1988; Schussler 63 et al., 2001). When high level waste (HLW) glass is corroded in Mg-rich brines, Mg- 64 bearing phyllosilicates form as part of the secondary phase assemblage (Strachan, 1983; 65 Strachan et al., 1984; Grambow and Muller, 1989; Maeda et al., 2011). Although 66 previously, and tentatively, identified as sepiolite (a member of the palygorskite family), 67 more recent investigations have identified trioctahedral smectites, such as saponite with 68 various stoichiometries, e.g., (½Ca,Na)0.66Mg6[(Si7.34Al0.66)O20](OH)4(e.g., Abdelouas et 69 al., 1997; Thien et al., 2010; Zhang et al., 2012; Fleury et al., 2013; Debure et al., 2016; 70 Aréna et al., 2017) as a reaction product. Note that in these more recent investigations, 71 the concentration of Mg in solution is relatively low (milli-molal range), in accord with 72 the dilute nature of pore water chemical compositions recovered from silicate-dominated 73 prospective repositories (e.g., Gaucher et al., 2009). Other investigations have shown 74 that when Mg-bearing glass, such as the British Magnox compositions, is altered in dilute 75 aqueous solutions the released Mg also leads to formation of Mg-smectite phases (e.g., 76 Curti et al., 2006; Thien et al., 2012; Harrison, 2014). It is likely, therefore, that saponite 77 could be a thermodynamically stable phase that precipitates when Mg-bearing solutions, 78 both dilute and concentrated, contact silicate glass for a sufficient length of time. 79 When saponite forms, it may impact the near-field chemistry of a geological 80 repository in various rock formations including salt formations by: (1) Controlling the 81 chemical compositions, including hydrogen ion concentrations, of the contacting 82 solutions, and (2) Forming a secondary mineral assemblage that will either enhance for 83 certain periods (Lucksheiter and Nesovic, 1998; Curti et al., 2006; Fleury et al., 2013; 5 84 Aréna et al., 2016, 2017), or retard (Grambow and Strachan, 1984; Frugier et al., 2005) or 85 both at different periods (Thien et al., 2012; Harrison, 2014), the dissolution rate of 86 glasses, and impact the retention of hazardous (radioactive) constituents after release 87 from the glass (e.g., Abdelouas et al., 1997). 88 In addition, because saponite has the swelling and sorption properties similar to 89 those of montmorillonite, saponite has also been proposed as a candidate buffer material 90 for HLW and spent nuclear fuel disposal in harsh environments (e.g., Yang et al., 2014). 91 This is because tri-octahedral smectites such as saponite have higher thermal and 92 chemical stabilities than di-octahedral smectites such as montmorillonite, and are less 93 susceptible to alteration in harsh environments (e.g., Eberl et al., 1978; Güven, 1990). 94 Because the phyllosilicates that form on the glass surface are typically not well 95 crystallized, and phase characterization efforts by X-ray diffraction are often technically 96 challenging, some investigators have resorted to using solution modelling to infer the 97 identity of candidate phases (c.f., Grambow and Müller, 1989). For this strategy to be 98 viable, knowledge of the thermodynamic properties of eligible phases, such as saponite, 99 is crucial. However, the thermodynamic properties of saponite, especially Mg-enriched 100 saponite, are not well-defined, and few studies have attempted to obtain them via glass 101 corrosion experiments (Aréna et al., 2017; Debure et al., 2016). For instance, in a recent 102 study, Aréna et al. (2017) tried to calculate the solubility constant of saponite (they called 103 it Mg-smectite) via geochemical modeling of their glass corrosion experiments. 104 However, their experiments were not designed, nor were they ideal, for determining the 105 solubility constants of saponite. Aluminum concentrations were very low in their 106 experiments, hampering modelling efforts. Hence, several compensating hypotheses 6 107 were constructed to estimate aluminum concentrations, including: (1) that aluminium 108 concentrations were equal to the quantification limit of the instrument (ICP-AES); (2) 109 aluminum concentrations were equal to the quantification limit divided by 1000; and (3) 110 aluminium was depleted stoichiometrically from saponite. These assumptions may not 111 be warranted. 112 Without accurate knowledge of the thermodynamic properties of saponite, it is 113 difficult to make reliable and accurate predictions for the evolution of chemical 114 compositions of the solutions containing Mg interacting with glass. Accurate knowledge 115 of its thermodynamic properties is thus the prerequisite for modeling glass corrosion in 116 Mg-bearing solutions, both at high and low ionic strength. 117 The objective of this study is to determine experimentally the solubility constants 118 of hydrous saponite at elevated temperatures under well constrained conditions. The 119 author first synthesized saponite (from nitrate cancrinite) according to an established 120 methodology (see Experimental Methods). Because hydrogen ion concentrations are a 121 key parameter governing the dissolution of saponite, the author first measured pH and 122 then applied correction factors obtained at elevated temperatures (Kirkes and Xiong, 123 2018). With proper knowledge of the hydrogen ion concentrations and the 124 concentrations of Al, Mg, Na and Si in solution, the author calculated the equilibrium 125 quotients. Then, the appropriate activity coefficient model is applied to extrapolate 126 equilibrium quotients at certain ionic strengths to infinite dilution. This model allows us 127 to then assess the solubility of saponite in previously reported experiments. It is shown 128 that an accurate log K value can be used to understand glass corrosion in Mg-bearing 129 solutions under a variety of geochemical conditions.